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DWR_2668843
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Last modified
10/8/2014 3:46:45 PM
Creation date
10/6/2014 11:31:29 AM
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Publications and Reports
Title
STREAM FLOW DATA FOR COLORADO
Year
2009
Document Type - Publications and Reports
Streamflow Report
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Discharge.-- <br />PLATTE RIVER BASIN <br />06701500 SOUTH PLATTE RIVER BELOW CHEESMAN RESERVOIR <br />Location.-- <br />Drainage and Period of Record.-- <br />Lat. 39°12'33",Long. 105°16'02", in SE¼NW¼ sec.6, T.10 S., R.70 W., Jefferson County, Hydrologic Unit 10190002, on left <br />bank 1,400 ft downstream from toe of Cheesman Dam and 3.8 mi southwest of Deckers. <br />1,752 mi². Oct.1, 1924-May 13, 1956 at site 370 feet upstream and 0.50 ft. higher. May 14, 1956 to present at <br />current site. Unreliable record from 1909 to 1924 unpublished. <br />Graphic water stage recorder and Sutron Satlink2 Data Collection Platform (DCP) with a Sutron 56-0540 shaft encoder <br />(SE) in a wooden shelter over a concrete well adjacent to a 30-foot concrete Parshall flume. The chart recorder was <br />replaced with a Sutron Stage Discharge Recorder (SDR) on September 10, 2009. No outside staff gage is present. The <br />station and flume are owned and maintained by the Denver Water Board (DWB). The satellite equipment is owned and <br />maintained by the Division of Water Resources (DWR). <br />Equipment.-- <br />Hydrographic Conditions.-- <br />Gage-Height Record.-- <br />Datum Corrections.-- <br />Rating.-- <br />Discharge.-- <br />Special Computations.-- <br />Remarks.-- <br />Recommendations.-- <br />Cheesman Reservoir is in the center of the 2002 Hayman burn area. The fire severely damaged the watershed and the <br />Denver Water Board has performed extensive erosion control in the area surrounding the reservoir. Major revegetation <br />efforts were performed in the burn area to reduce erosion and water quality problems. <br />The primary record is hourly averages of 15-minute telemetered SE data with chart and SDR data as backup. The DCP <br />suffered various failures of short duration or required maintenance throughout the year which caused the log to be <br />incomplete. Data gaps occurred on: October 1 and 23, 2008; November 6, 7, 15, 16, 26, 2008; Dec 1, 2008; and August 4 <br />-5, 2009. These gaps were filled in with chart data without loss of accuracy. Some interpretation of the exact time was <br />occasionally required with the chart record (due to poorly adjusted clock), but this was accomplished with complete <br />accuracy by bracketing change periods. Twenty-six visits were made to the gage and no SE adjustments were needed. <br />Due to the flume’s proximity to the dam, ice accumulation in the approach, flume, and departing sections is not an issue. <br />However, the flume is subject to moss and algal growth. Two flume cleaning corrections were made: -0.01 feet on <br />October 20, 2008, prorated by time as a datum correction from the previous visit (date) when the flume was cleaned; and - <br />0.10 ft on February 24, 2009 addressed by incorporating the correction into shift for the measurement made that day. <br />Levels were run on September 10, 2009 and the gage was found to be reading correctly. <br />The control is a concrete 30-foot Parshall flume with a modified rating. The flume submerges at flows near the 1000 cfs due <br />to constrictions in the channel below the gage. Rating No. 11 was developed in 1995 to compensate for submergence and <br />was continued in use for the current year. Submergence seems to begin when the measurement section velocity reaches <br />around 6.6 ft/s. The rating is well defined except for flows around 1,000 cfs where submergence appears to cause a break <br />point in the slope of the curve. Shifts historically were within a few hundredths of the rating. However as the approach pool <br />has filled, shifts have become more positive. Gravel deposition occurred on the left side of the upstream channel and the <br />flume converging section during a precipitation event on 7/21/2009. The gravel was washed down the access road into the <br />channel above the Parshall flume. Some effort was made to remove the material when the road was repaired; however a <br />large delta remains causing higher velocities from the mid section to right edge of water in the flume. Comparisons of <br />velocities to measurements taken in 1995 show the effects of the approach pool filling with elevated velocities at <br />comparable depths. Using the USBR "Water Measurement Manual", a 30 ft Parshall Flume's range of accurately <br />measuring discharge is 15 to 1500 cfs. Anything above or below this range is outside the +/- 5% accuracy. Given this fact, <br />flows below 15 cfs at gage height 0.38, or above 1500 cfs at gage height of 5.94 the record would be considered fair. All <br />flows in water year 2009 were within the +/- 5% range of accuracy. Twenty three measurements (Nos. 205-227) were <br />made during the water year ranging in discharge from 37.9 to 878 cfs. The flume rating is well defined for the ranges of <br />flow experienced. The peak discharge of 900 cfs occurred at 1630 June 3, 2009 at a gage height of 3.52 ft with a shift of <br />+0.19 ft. It exceeded measurements Nos. 219, 220, made on June 4, 2009, by 0.06 feet in stage. <br />Shifting control method was used all year. Negative shifts occur when moss accumulates on the crest of the flume. This <br />was the case for the periods from 10/1/2008 to 2/24/2009 and from 9/2/2009 to 9/30/2009 when moss was noted to affect <br />the stage discharge relationship. Shifts were applied as defined by measurements and distributed by time for this period. <br />For the period from 2/24/2009 to 9/2/2009, variable shift table PLACHECOVST1 was applied with shifts distributed by <br />stage. PLACHECOVST1 was developed from measurements # 212 through # 226 completed during the same period. <br />Measurements 217 abd 223 were adjusted 1% and 2% to better fit the shift curve. Measurements for the entire water year <br />show shifts varying from -0.05 ft. to 0.19 ft. <br />Flume cleaning corrections are handled differently depending on whether the State or DWB perform the cleaning. If the <br />gage height drops as a result of a DWB flume cleaning, it usually occurs between measurements, it is Denver’s procedure <br />to increase the release so that the same gage height is maintained. This did not occur this year. If a gage height change <br />occurs when the flume is cleaned by a State Hydrographer, a measurement is made before and after the flume cleaning <br />with shifts applied accordingly. <br />The record is considered good. Station maintained and record developed by Mike Wild . <br />Remove gravel from weir pool. Install staff gage. <br />2009Water Year
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